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SR0085397_SSNL
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SR0085397_SSNL
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Last modified
7/8/2022 9:39:41 AM
Creation date
6/30/2022 1:17:16 PM
Metadata
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Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSNL
RECORD_ID
SR0085397
PE
2602
STREET_NUMBER
23751
Direction
S
STREET_NAME
BIRD
STREET_TYPE
RD
City
TRACY
Zip
95304
APN
25010015
ENTERED_DATE
6/13/2022 12:00:00 AM
SITE_LOCATION
23751 S BIRD RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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The project site has level terrain; consequently, there is no need to incorporate design <br /> considerations for slopes within the effluent disposal area. <br /> B. SOIL PHYSICAL CHARACTERISTICS AND ANALYTICAL TEST RESULTS <br /> SSS§ 5.2. The UC Davis Soil Web designates the soil as a Capay Clay(#118): 85% Capay clay, <br /> 5% Stomar clay, 4% Willows clay, 4%Vernalis clay. Texture analysis show the soils at 36" below <br /> grade in the proposed filter bed area to be a clay loam (clayey silt). <br /> NLS§ 1.1, 1.2. The surface and subsurface soil investigation began on May 24, 2022 with-the <br /> drilling of one 36-inch deep perc test boring. Auger cuttings were sampled for laboratory analysis <br /> from this depth. •As noted on the Soil Report in Appendix B, chemical analysis of the soil samples <br /> quantifies a number of constituents that influence nitrate loading for this project. The important <br /> parameters for nitrate loading assessment are the organic matter,pH, cation exchange capacity <br /> (CEC), and the nitrate-nitrogen content of the soil. Additional chemistries were also conducted for <br /> loading assessment including the carbon-nitrogen(C:N)ratio, organic carbon and Total Nitrogen <br /> (TN). Although the TN was relatively high, the C:N ratio was 8.2 which is low enough to impede <br /> nitrification and promote denitrification. <br /> The soil nitrate-nitrogen concentration is a medium concentration at 13 ppm at the 36" depth. The <br /> subject property has not been under agricultural production since approximately 2007, so the <br /> nitrogen concentration is residual from previous production agriculture and organic decomposition <br /> of native grasses. <br /> Because septic effluent is composed predominately of ammonium(NH4),the pH, along with the <br /> CEC, are significant influences on the ammonium m6lecules. The pH of the soil profile is alkaline at <br /> 7.4. At this pH, ammonium will have a slight propensity to convert to ammonia. The CEC measures <br /> the ability of the soil to theoretically trap and hold ammonium molecules and is high at 26.7 <br /> meq/100g. <br /> NLS§3.3, SSS§ 5.3,5.4. Table 1 below summarizes the soil physical and chemical <br /> characteristics for the proposed filter bed soil: <br /> TABLE 1 <br /> SOIL PROFILE CHARACTERISTICS AND <br /> ANALYTICAL TEST RESULTS <br /> SAMPLE DEPTH AND SOIL SOIL NITRATE- pH,CATION EXCHANGE <br /> (SAMPLE ID ON TEST CLASSIFICATION NITROGEN CONTENT CAPACITY <br /> RESULT FORM) TKN CONTENT <br /> FILTER BED Clay Loam 13 ppm NO3-N 7.4 26.7 meq/100- <br /> 36"DEPTH <br /> (36'x) 760 mg/kg <br /> Chesney Consulting <br />
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